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PR0544148
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Last modified
2/14/2019 6:16:53 PM
Creation date
2/14/2019 2:56:21 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
WORK PLANS
RECORD_ID
PR0544148
PE
3526
FACILITY_ID
FA0005937
FACILITY_NAME
NEAL STALLWORTH AUTO DETAIL
STREET_NUMBER
602
Direction
N
STREET_NAME
CALIFORNIA
STREET_TYPE
ST
City
STOCKTON
Zip
95202
APN
13916509
CURRENT_STATUS
02
SITE_LOCATION
602 N CALIFORNIA ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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i <br /> 25 July 2008 <br /> AGE-NC Project No. 99-0682 <br /> Page 3 of 6 <br /> impacted soil at the site; wells VW- I and VW-3 are screened through the lower vadose zone (20 feet <br /> to 30 feet bsg) and VW-2 and VW-4 are screened through the shallow vadose zone (10 feet to 20 feet <br /> bsg). Based on the results of the SVE pilot tests conducted at the site in July 2008, a theoretical <br /> radius of influence (ROI) of lowervadose SVE at the site will be approximately24 feet; a theoretical <br /> ROI of upper vadose SVE at the site will be approximately 24 feet. Utilization of wells VW- 1 <br /> through VW-4 for an interim remediation SVE system should be adequate to extract soil vapor from <br /> the petroleum-impacted soil in the vadose zone beneath the former UST area. <br /> 2.3 . INSTALLATION OF INTERIM REMEDIATION SYSTEM PIPING NETWORK <br /> Remediation system piping network will be installed underground within a 1 -foot wide by 1 '/z-foot <br /> deep trench. In order to minimize flow restrictions and more readily facilitate the reconfiguration of <br /> the SVE wells, AGE proposes to install separate piping runs (home-runs) composed of 2-inch <br /> diameter, schedule 40 PVC piping from well-heads at VW- 1 through VW-4 to an extraction <br /> manifold located inside the proposed remediation enclosure. From the extraction manifold, 2-inch <br /> diameter, schedule 40 PVC piping will be routed to the proposed soil vapor extraction unit <br /> (thermal/catalytic oxidizer). Following piping placement, the trench willbe backfilled with imported <br /> road-base sand, compacted, and resurfaced to grade with asphalt. <br /> The proposed underground trenching location is depicted on Figure 3 ; a cross sectional view of the <br /> trench is depicted on Figure 4; a diagram depicting the proposed extraction manifold is illustrated <br /> in Figure 5 . <br /> 2.4 . PROPOSED INTERIM SOIL REMEDIATION SYSTEM <br /> The proposed SVE treatment unit will be a Mako Industries 250 TCAT (or similiar), which is <br /> comprised of a condensation separator, a vacuum blower, a thermal/catalytic oxidizer, and control <br /> components . The 2-inch diameter home-run piping installed from the well-heads at VW-1 through <br /> VW-4 will be connected to the inlet of the condensation separator, which leads into the vacuum <br /> blower;, the outlet fromthe vacuumblowerwillbe routedthrough a thermal heated catalytic oxidizer. <br /> The 250 TCAT would be modified for catalytic oxidation with the current concentrations below <br /> 3 ,500 parts per million volume (ppmv) . <br /> Induced vacuum will be measured utilizing a Magnehelic vacuum gauge attached to the inlet of the <br /> blower; SVE air flow will be monitored using a Dwyer DS-200 flow sensor. Sampling ports will be <br /> installed upstream of the vacuum blower inlet to recover SVE influent air flow vapor stream <br /> samples, and downstream of the oxidizer to recover effluent SVE air flow samples and to monitor <br /> the efficiency ofhydrocarbon destruction. A schematic diagram of the SVE treatment unit is depicted <br /> Advanced GeoEnvirontnental, Inc. „. <br />
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